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Management of Commercially Generated Radioactive Waste - U.S. ...

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6.11<br />

bridge crane would remove the loaded shipping cask and move it to the confinement section <strong>of</strong><br />

the building. The lid would be removed and the cask aligned with a hot cell port. The HLW<br />

or spent fuel canisters would be removed remotely to a storage rack within the hot cell.<br />

An interim dry storage area adjacent to the hot cell would have space for a 1-month sup-<br />

ply <strong>of</strong> canisters.<br />

The hot cell would include space for checking the canisters for visible damage, radia-<br />

tion leakage, and surface temperature. Facilities would be provided to decontaminate waste<br />

handling equipment in case <strong>of</strong> a canister failure. Damaged canisters would be overpacked and<br />

returned to the processing and emplacement facility for repacking.<br />

The receiving facility would also provide auxiliary services such as ventilation, equip-<br />

ment maintenance, and a control system.<br />

Canister Transporters. Canister transporters, similar to those used for subsurface<br />

transportation and emplacement in the mined geologic repository (Section 5.4), would be used<br />

to transfer the waste from the receiving facility to the emplacement facilities. Each trans-<br />

porter would consist <strong>of</strong> a wheeled vehicle suitable for operation on site roadways, a shielded<br />

transfer cask, and equipment for raising and lowering canisters in and out <strong>of</strong> the transfer<br />

cask. In the receiving facility, the transporters would be positioned over a portion <strong>of</strong> the<br />

hot cell to bottom load the canisters into the transfer cask. At the emplacement facility,<br />

the transporters would be positioned over the temporary storage area and the canisters would<br />

be bottom discharged into temporary storage.<br />

Drilling System. The drilling rigs would be similar to those used in the gas and petro-<br />

leum industries and would be portable for movement from one hole location to another on the<br />

site. Each complete rig would require a clear, relatively flat area, approximately 120 x 120<br />

m (400 x 400 ft), at each hole location (McClean 1977).<br />

In the reference concept, the drilled hole for spent fuel is 48 cm (19 in.) in diameter<br />

and 10,000 m deep (Bechtel 1979a). For HLW, the hole is 40 cm (16 in.) in diameter. The<br />

depth and diameter, however, could vary depending on the geologic medium, the depth required<br />

to satisfy containment requirements, and the drill rig capacity. For HLW, the hole would be<br />

fully cased to the required depth with seamless steel pipe about 40 cm in outside diameter,<br />

which would reduce the hole diameter available for waste.<br />

Oil field rotary drilling techniques would be used to sink the holes, which may be step-<br />

ped down in diameter as the depth increases. To seal the pipe to the rock, a grout would be<br />

forced through the pipe and then back up between the wall <strong>of</strong> the hole and the outside <strong>of</strong> the<br />

casing. The bottom <strong>of</strong> the hole would be sealed.<br />

During the drilling and emplacement operation, the hole would be kept full <strong>of</strong> drilling<br />

mud to facilitate drilling, prevent casing and canister corrosion, minimize casings sticking<br />

to the sides <strong>of</strong> the hole during installation, and counter lithostatic pressure.<br />

Emplacement Facilities. Each emplacement facility would include a confinement enclosure<br />

to provide a controlled environment for emplacement operations, and the temporary canister

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